HomeMy WebLinkAboutWetland Delineation 821182003
Olympic Wetland Resources
Lou Slagle
Wetland Delineation Report
April 2000
Prepared for
Lou Slagle
2203 Beaver Valley Road
Port Ludlow, WA 99365
Prepared by:
Dixie Llewellin, Principal Biologist
Olympic Wetland Resources, Inc.
856 50th Street
Port Townsend, W A 98368
Lou Slagle
Wetland Delineation Report
Contents
Description of Site
Introduction
Methodology
Classification and Jefferson Critical Areas
Ordinance Soils
Vegetation
Hydrology
Findings
Wetland Edges
Classification and Jefferson Critical Areas
Ordinance
Soils
Vegetation
Hydrology
Recommendations
Summary
References
Appendix
Maps
Figure I: Location Map
Figure II: Wetland Delineation
Figure III: Jefferson County Critical Areas
Figure IV: Jefferson County Soil Survey
Corp of Engineer Wetland Data Sheets
Lou Slagle
Wetland Delineation Report
April 28, 2000
Description of Site
. Legal Description: Section 18, Township 28, Range 1 East WM; APN 821182003
. SlopelElevation: 0 to 15%
. Location: 2203 Beaver Valley Road, one half mile south of Beaver Valley Store
(Location Map Figure I Appendix)
. Soils: EvD Everett gravelly sandy loam and Mm McMurray and Mukilteo Peat
Introduction
At the request of Lou Slagle, Dixie Llewellin of Olympic Wetland Resources, Inc. conducted a
wetland delineation on April 26, 2000. The 53-acre site is located in Beaver Valley (2203 Beaver
Valley Road) west of Highway 19. This wetland survey is precursory to a building permit
application for a manufactured home installation to be located near the wetland. The results of this
report will also affect the placement of an existing structure, which has been referred to as "Fred's"
mobile home (letter to Lou Slagle March 29,2000 from Michelle Farfan, Assistant Planner Jefferson
County Department of Community Development). The portion of the wetland surveyed lies directly
west of the existing mobile homes. The scope of this delineation was to determine the area of the
wetland and buffers that would affect final placement of the manufactured home.
The wetland will be considered a Class I wetland due to the large size, forest cover, and connections
to a fish-bearing stream.
Development adjacent to wetlands or within wetland buffers is subject to regulation standards of the
Jefferson County Critical Areas Ordinance and the Corps of Engineers.
Methodology
Prior to the fieldwork, the following maps were consulted:
. National Wetland Inventory Maps
. U.S. Geological Survey Maps
. Jefferson County Critical Areas Maps (Figure ill Appendix)
. Soil Survey Maps of Jefferson County (U.S. Soil Conservation Service 1975) (Figure IV Appendix)
Fieldwork to determine the actual wetland boundaries was conducted according to the methodology
outlined in the Washington State Wetland Identification and Delineation Manual (Department of Ecology
#96-94). Washington Administrative Code requires that all wetlands within the State of Washington be
delineated using this manual.
Examination of three parameters is required for a positive wetland determination: hydric soils, hydrophytic
vegetation, and hydrology. For an area to qualify as a jurisdictional wetland it must have a positive
indicator from all three parameters. All wetlands which meet the criteria, regardless of size, may be
federally regulated.
Lou Slagle Wetland Report
2000-52
1
Olympic Wetland Resources, Inc. 4/00
Classification and Jefferson Critical Areas Ordinance
Wetland categorization was determined using the Washington State Department of Ecology Wetland
Rating System (publication #91-57 October 1991), which assigns a numerical value to any given wetland
according to wetland size, quality of surrounding buffers, vegetation diversity, wetland types, and habitat
value. Wetlands are rated as entire systems and quite often extend beyond project boundaries.
All wetlands are regulated by the most recent Jefferson County Critical Areas Ordinance (1995)
wetlands are regulated if they meet certain sizes and classifications.
Soils
A hydric soil is a soil that formed under conditions of saturation, flooding, or ponding long enough
during the growing season to develop anaerobic condition in the upper part. Hydric soils favor the
growth and regeneration ofhydrophytic vegetation. The indicators for this type of soil include low
chroma, mottles, gleying and high organic content within the upper 32 inches of the soil profile. Holes
were dug on the site and soil colors (including value and chroma) were recorded in the top 16 inches to
determine wetland soils. Soil colors were analyzed using the Munsell Color Charts (1992).
Vegetation
Wetland plant species must constitute greater than 50% of the total vegetation present to meet the
qualification as a site dominated by hydrophytic vegetation. Dominance of plant species is determined by
calculating actual aerial cover within a 3D-foot radius for trees, a lO-foot radius for shrubs and a 6-foot
radius for the herbaceous layer at each data point. Each species was recorded and given a rating
according to its indicator status as described by the United States Fish and Wildlife Service, National List
ofFlant Species that occur in Wetlands: Northwest (Region 9).
Hydrology
Wetland hydrology is defined as "areas that are periodically inundated or have soils saturated to the
surface at some time during the growing season". Areas must have seasonally inundated or saturated soils
at least 12.5% of the growing season. 1 Indicators of hydrology include visual observation of inundation
or soil saturation, water-stained leaves, cracking at the soil suITace or sediment deposits. Positive signs of
hydrology are often absent during the summer and fall months but can be inferred if there are positive
indicators of hydric soil and hydrophytic vegetation.
Findings
Wetland Edges
Boundaries were determined by establishing data points within the wetland, which contained positive
indicators of all three of the wetland requirements; and data points outside the wetland, where wetland
soils, hydrology or hydrophytic vegetation were not present. Data point locations are shown on the
Wetland Delineation Map in the Appendix (Figure 11).
1 The growing season is defined by the Jefferson County soil survey as March 12 to November 25 in or near Port
Townsend. Hydrology must be present for 12.5% (20 days) of these 258 days for an area to qualifY as a wetland.
Lou Slagle Wetland Report 2 Olympic Wetland Resources, Inc. 4/00
2000-52
On April 26, 2000 wetland edges were flagged with orange Wetland boundary tape (AI through
All) at 25 to 50 foot intervals. All data points and soil test pits were also flagged. Information for
all data points was recorded and is included in the Corps of Engineers Data Forms in the Appendix.
Wetland boundaries, data points, and approximate structure locations are shown on the Wetland
Delineation Map in the Appendix (Figure II).
The natural wetland buffer has been altered 8 to 10 years ago by adding a berm containing fill to
accommodate the structures (conversation with Lou Slagle 11/15/99). There is a definite
topographic rise between the fill and the wetland to the west, as well as a distinct plant community
change. Soils, hydrology, and plant change also verity the wetland/upland edge, which generally
runs along the base of the berm. On the northern edge of the property, the soil and wetland edge is
less disturbed; soil pits verity the edge. There are two man-made ponds on the property that
overflow towards the wetland.
Classification and Jefferson Critical Areas Requirements
According the Jefferson County Critical Areas map (verified by on-site findings) a Class I wetland
exists to the west and north of the structures on the Slagle property. This wetland is large, spreading
throughout Beaver Valley, and is connected to fish-bearing streams (Ludlow Creek and near the
headwaters of Chimacum Creek). This wetland along the valley bottom includes a significant wildlife
habitat movement corridor, has a forested class, and contains significant habit features such as
standing dead trees. Class I wetlands receive the highest protection and require a maximum of75
feet buffer from the wetland edge (Low Intensity Land Uses Jefferson County Critical Areas
Ordinance 6.505-5).
Buffer averaging (Subsection 6.508, with the criteria of Subsection 11.1002, Jefferson Critical Areas
Ordinance) will be an option only when the wetland functional values are not compromised. The
total area contained within the wetland buffer should be equal to or greater than the buffer sacrificed.
The standard buffer width cannot be reduced by more than fifty percent. A Class I wetland buffer
shall under no circumstances be less than 38' wide.
It should be noted that the boundary flagged represents only a small portion of this wetland, which
continues to the south and to the north and extends well beyond the subject property.
Soils
Soils EvD Everett gravelly sandy loam and Mm McMurray and Mukilteo Peat. McMurray and
Mukilteo Peat are soils are listed on the Jefferson County Hydric Soils List.
T est pits were dug to a depth of 16 inches in the wetland area and inspected for hydric conditions.
Highly saturated soils were located at Data Points #1, #3, and #6 and at Soil Test Pit #4. Top layers
of deep brown (lOYR 3/1), gleyed (bluish gray) colored soil (5/10Y), and orange mottling were
observed in the wetland soil pits. All soil colors identified meet the requirements of hydric soil. An
upland test pit was dug to a depth of 16 inches; soil colors did not quality as hydric (lOYR 3/4 with
mottles) .
Corp of Engineer Data forms for all Data Points are included in the Appendix.
Lou Slagle Wetland Report
2000-52
3
Olympic Wetland Resources, Inc. 4/00
Vegetation
Vegetation in the wetland areas includes a mixed deciduous tree layer of alder and two species of willows
with an understory of salmonberry, cattail, sedges, water parsley, nettles and buttercups. Several of these
species require regular inundation. Reed canarygrass, a non-native and often invasive grass, is present
along the wetland edge. The upland area is mostly cleared to accommodate the living areas.
Hydrology
There is a flowing stream, Ludlow Creek, at the bottom of the valley with areas of pooled water in
the adjacent wetland. Soil saturation and surface saturation were prevalent for 160 feet from the
creek. All of the wetland test pits had water within 3" to 10" of the surface.
Recommendations
Buffer averaging should include a buffer enhancement plan which specifies the introduction of native
trees and shrubs to increase the diversity and functional attributes of the buffer. The control of the
reed canarygrass, and removal of debris from the wetland (metal roofing, lumber piles, debris) is also
recommended. Any planting should be monitored at least 5 years to ensure success.
Summary
A Class I wetland is present on the Slagle property and buildings will be regulated according to the
Critical Areas Ordinance concerning wetlands. Buffers for Class I wetland are 75 feet. Reduction of
buffers is possible but shall be allowed only when specified criteria are met.
Final authority over this wetland determination and classification rests with Jefferson County and the
Corps of Engineers.
If you have any questions please feel free to call.
Dixie Llewellin
Principal Biologist, Olympic Wetland Resources, Inc.
Certified for Wetland Delineation, 1987 Manual
Wetland Training Institute June 1995.
Lou Slagle Wetland Report
2000-52
4
Olympic Wetland Resources, Inc. 4/00
References
Literature Cited
Cooke, Sarah Spear, 1997. A Field Guide to the Common Wetland Plants of Western
Washington and Northwest Oregon. Seattle Audubon Society. Seattle, WA.
Cowardin, L.M.Y Carter, F.C.Goblet, and E.T. LaRoe, 1979. Classification of Wetland and
Deep Water Habitats of the U.S. Fish and Wildlife Service. Washington, DC. 1979
Hitchcock and Conquest, 1973. Flora of the Pacific Northwest.
Federal Interagency Committee for Wetland Delineation, 1987. Federal Manual for Identifying
and Delineation Jurisdictional Wetlands. July 1994 update. U.S. Army Corp of
Engineers, U.S. Environmental Protection Agency, U.S. Fish and Wildlife Service, and
U.S.D.A. Soil Conservation Service.
Guard, Jennifer, 1995. Wetland Plants of Oregon and Washington. Lone Pine Press.
Redmond, Washington.
Jefferson County Critical Areas Ordinance, May 1994
Leonard, William P., 1993. Seattle Audubon Series. Amphibians of Washington and Oregon.
MacBeth, Div. of Kollmorgen Instruments Corp., 1992 Munsell Soil Color Charts.
Mitsch and Gosselink, 1993 Wetlands.
Pojar, Mackinnon, 1994. Plants of the Pacific Northwest Coast.
Reed, Porter, 1988. National List of Plant Species that Occur in Wetlands, Region 9. 1993
update.
Washington State Wetland Department of Ecology. March, 1997. Washington State Wetland
Identification and Delineation Manual, #96-94.
U.S.D.A., Dept. of Agriculture. 1994 Pocahontas Press. Keys to Soil Taxonomy.
U.S.D.A., Soil Conservation Service, 1975. Soil Survey of Jefferson County.
Location Map
Figure I
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i. Location Map Figure I
.. 856 50th street April 2000
Port lownsend, WA 98368 (Iien~ Lou Slagle
360 385.6432 2203 Beaver Valley Road Job #: 2000-52
.J u Port Ludlow, WA 98368
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Port Jownsend, WA 98368
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Wetland Delineation
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Wetland
[ilk: Lou Slagle
Wetland Delineation
(Iien~ Lou Slagle
2203 Beaver Valley Road
Port Ludlow, WA 98368
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Job #: 2000-52
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Jefferson County Soi I Survey Map
Jefferson County, Washington
1915
US Department of Agriculture
Soil Conservation Service
All locations approximate
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figure IV
Critical Areas Map
Figure III
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Jilk: Lou Slagle
Wetland Delineation
Critical Areas Map
April 2000
Scole:
C1ien~ Lou Slagle
2203 Beaver Valley Road
Port Ludlow, WA 98368
Job #: 2000':52
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t
~heet
Figure III
Date: 41zCe/ DD
County:. 'J6F~
State: W A
Srr/R: 2.8N R. l E.
Community ID:
Transect ID:
Plot ID: pp4f I
Dominant Plant S ecies
Stratum % cover Indicator Dominant Plant S ecies
Stratum % cover
Indicator
r
T
5
30
ftk.
PA<:..
L
I 5f' (D
HYDROPHYTIC VEGETATION INDICATORS:
% of dominants OBL, FACW, &FAC ~
Check all indicators that apply & explain below:
Visual observation of plant species growing in ..J
areas of prolonged inundation/saturation "
Morphological adaptations
Technical Literature .L..
Hydrophytic vegetation present? yes no
Rationale for decision/Remarks: ~ "'i
~f::2Mtl- ~e5 CF D6U'ittre \t~,e:-In,~vl .
Physiological/reproductive adaptations
Wetland plant database
Personal knowledge of regional plant communities
Other (ex lain)
')(.
~
HYDROLOGY
Is it the growing season?
@
no
Water Marks: yes no
on
Drift Lines:
Sediment Deposits: yes no
Based on: ~ soil temp (record temp. )
other (ex lain)
Dept. of inundation: ~ inches
yes no
Drainage Patterns: yes no
Depth to free water in pit: L inches
Depth to saturated soil: ~ ()~ inches
Check all that apply & explain below:
Stream, Lake or gage data:
Aerial hotoora hs:
Wetland hydrology present?
Rationale for decision/Remarks:
WJ\1e1- P~f"
Oxidized Root (live roots)
Channels <12 in. es no
FAC Neutral: yes no
Local Soil Survey: yes no
Water-stained Leaves yes no
Other (explain):
Other:
C!!V
no
SOILS
Map Unit Name (Y\m 1\1.... MuR!-AY st M c/Kt'-,ev Pt:.~ Drainage Class II \AI
(Series & Phase)
Pic.... fYIE[)
roT
Field observations confirm
d e?
@
No
Profile Description
Depth Horizon Matrix color Mottle colors Mottle abundance Texture, concretions, Drawing of soil
(inches) (Munsell (Munsell size & contrast structure, etc. profile
moist) moist) (match descriPtion)
D-(P (o'(~ 'II - -
~w~
.... J . . ~ L
V ~n'''''''
.
.
Hydric Soil Indicators: (check all that apply)
_ Histosol ~ Matrix chroma :s 2 with mottles
_ Histic Epipedon _ Mg or Fe Concretions
~ Sulfidic Odor _ High Organic Content in Surface Layer of Sandy Soils
_ Aquic Moisture Regime _ Organic Streaking in Sandy Soils .
_ Reducing Conditions ~ Listed on NationallLocal Hydric Soils List
Gleyed or Low-Chroma (=1) matrix Other (explain in remarks)
Hydric soils presen.t? ~ no
Rationale for decisionlRemarks:
Wetland Determination (circle) '.
Hydrophytic vegetation present? ~ no
Hydric soils present? es no Is the sampling point Sf!!) no
Wetland hydrolo~ present? .~ no within a wetland?
RationaIelRemarks: 1lftS ~~ raM, (S ""'" 2<5' '.1--U::~lSr of ,. F~J:}S " TfJ-At L6L.
NOTES:
Revised 4/97
1987 Corns Wetland Delineation anu
Project/Site: LoO ~ LE Date: 4/Z~ / DO
2 2 () ~ e~'/€;(L.. V A-LLe't (?pAP '. County:, 'JCFf1:;::r2.Sotv
Applicant/owner: ~L-\JO~ v-.JA q~'3(,,'i' . ,.
State: W A
Investi.e;ator(s): D.I I I::i Ifl F:1 I IAt D r....'f M "11' \A ._.A RJ;;SDJ u.e5> srr/R: SIR r Z8"N ~lE
Do Normal Circumstances exist on the site? yes no Community ID:
Is the site significantly disturbed (atypical situation)? yes no Transect ID:
Is the area a potential Problem Area? yes no Plot ID: Df4fz-
Explanation of atypical or problem area:
VEGETATION (For strata, indicate T = tree; S = shrub; H = herb; V = vine)
Dominant Plant SpeCies Stratum % cover Indicator Dominant Plant Species Stratum % cover Indicator
DA........ ICUUJ,S ~\::1'~ H 7'5 ~v..I
F=~1VcA Pt2A'P:N~)~ L4 25" .l7\c.>>
.
HYDROPHYTICVEGETATION INDICATORS:
% of dominants OBL, FACW, & FAC 75"
Check all indicators that apply & explain below:
Visual observation of plant species growing in -- Physiological/reproductive adaptations -
areas of prolonged inundation/saturation Wetland plant database ~
Morphological adaptations - Personal knowledge of regional plant communities ~
Technical Literature Other (explain)
Hydrophytic vegetation present? @ no
Rationale for decisionlRemarks:
HYDROLOGY
Is it the growing season? @ no Water Marks: yes no Sediment Deposits: yes no
on
Based on: D~ soil temp (record temp ) Drift Lines: Drainage Patterns: .
yes no yes no
other (explain)
Dept. of inundation: ~ inches Oxidized Root (live roots) Local Soil Survey: yes no
Channels <12 in. yes no
Depth to free water in pit: N~ inches FAC Neutral: yes no Water-stained Leaves yes no
Depth to saturated soil: N.~ inches
Check all that apply & explain below: Other (explain):
Stream, Lake or gage data: -
Aerial photo.e;raphs: Other:
Wetland hydrology present? yes ~
Rationale for decisionlRemarks:
DATA FORM 1 (Revised)
Routine Wetland Detennination
(W A State Wetland Delineatiop Manual or
M al)
SOILS
Map Unit Name m m f'Y1, I' fYl () ~ y st M cll4c.:1t=D Pc"1\'r:) Drainage Class t I \A./
(Series & Phase)
Pic.. /YlEp
ror
Field observations confirm
ma ed e?
~~
Profde Description
Depth Horizon Matrix color Mottle colors Mottle abundance Texture, concretions, Drawing of soil
(inches) {Munsell (Munsell size & contrast structure, etc. profile
moist) moist) (match description)
0-12. tI I 0((2. ~+ ~O~ ((.otll-'1 I
Mc~ tl' r: ,LA.U~ - -
1
&.-
Hydric Soil Indicators: (check all that apply)
- Histosol _ Matrix chroma S; 2 with mottles
_ Histic Epipedon _ Mg or Fe Concretions
- Sulfidic Odor _ High Organic Content in Surface Layer of Sandy Soils
_ Aquic Moisture Regime _ Organic Streaking in Sandy Soils
_ Reducing Conditions _ Listed on Nationa1/Local Hydric Soils List
Gleyed or Low-Chroma (=1) matrix Other (exolain in remarks)
Hydric soils present? yes ~
Rationale for decisionlRemarks:
Wetland Determination (circle)
Hydrophytic vegetation present? if!D no
Hydric soils present? yes ~ Is the sampling point yes ~
Wetland hydrology present? yes ~<<ro:) within a wetland?
RationalelRemarks: lttts AAt""'A (":> 1'{E;X. i \D .. 'F~" 172--1'\1 LtVL. - ~ c.6M S 1575
DF f1LL .
NOTES:
Revised 4/97
Investi ator( s): 1-l...e:5>
Do Normal Circumstances exist on the site? yes no
Is the site significantly disturbed (atypical situation)? yes no
Is the area a potential Problem Area? yes no
Ex lanation of at ical or roblem area:
VEGETATION (For strata, indicate T = tree; S = shrub; H = herb; V = vine)
Date: 4/ z!e I () {)
County:. 'JCF~
State: y../ A
srrlR:
Community ID:
Transect ID:
Plot ID:
Z8N ~ l E.
Dp.:# 3
Dominant Plant S eCies
Stratum % cover Indicator Dominant Plant S ecies
Stratum % cover
Indicator
Ib
Zo
to
HYDROPHYTIC VEGETATION INDICATORS:
% of dominants OBL, FACW, & FAC l 00 Cf b
Check all indicators that apply & explain below:
Visual observation of plant species growing in
areas of prolonged inundation/saturation ~
Morphological adaptations
Technical Literature
Hydrophytic vegetation present?
Rationale for decisionlRemarks:
Physiological/reproductive adaptations
Wetland plant database
Personal knowledge of regional plant communities
Other (ex lain)
.:L
-:>C
HYDROLOGY
Is it the growing season?
@ no
Water Marks: yes no
on
Drift Lines:
Sediment Deposits: yes no
Based on: ()/Jffl;; soil temp (record temp.
other (ex lain)
Dept. of inundation: ~ inches
yes no
Drainage Patterns: yes no
"
~ inches
inches
Oxidized Root (live roots)
Channels <12 in. es no
FAC Neutral: yes no
Local Soil Survey: yes no
Depth to free water in pit:
Depth to saturated soil:
Check all that apply & explain below:
Stream, Lake or gage data:
Aerial hotoura hs:
Wetland hydrology present?
Rationale for decisionlRemarks:
Water-stained Leaves yes no
Other (explain):
Other:
~
no
SOILS
Map Unit Name m m lY1 '" MaRltAy st /YlllKL'-?eD ~~ Drainage Class II \AI
(Series & Phase)
PiC- fYlEp
l'5T
Field observations confirm
ffia d e?
@)
No
Profile Description
Depth Horizon Matrix color Mottle colors Mottle abundance Texture, concretions, Drawing of soil
(inches) (Munsell (Munsell size & contrast structure, etc. profile
moist) moist) (match descriPtion)
0...(" IOrR 4fz ~1fC'? :n.~ 1..
...,
Co-( " \ c'( (L 4( 2- U::x; flSe
(0
^^A. 1
Hydric Soil Indicators: (check all that apply) --.L::::: Matrix chroma ~ 2 with mottles
_ Histosol
_ Histic Epipedon _ Mg or Fe Concretions
_ Sulfidic Odor _ High Organic Content in Surface Layer of Sandy Soils
_ Aquic Moisture Regime _ Organic Streaking in Sandy Soils
~Reducing Conditions -->'- Listed on NationallLocal Hydric Soils List
Gleyed or Low-Chroma (=1) matrix Other (explain in remarks)
Hydric soils presen.t? !ffj) no
Rationale for decisionlRemarlcs:
Wetland Determination (circle) ~
Hydrophytic vegetation present? d~ no
Hydric soils present? ~ no Is the sampling point @:> no
Wetland hydrology present? no within a wetland?
RationaleJRemarks:
NOTES:
Revised 4/97
DA T A FORM 1 (Revised)
Routine Wetland Determination
(W A State Wetland Delipeatiop Manual or
1987 Co s Wetland Delineation Manual)
Project/Site: LoO SL.N1 L.E
.2 20? 'Bt:$.'/etL V AUet r'O>M
Applicant/owner: fbr1;t L\IO~ ,^,A q~'3" 't
Date: 41Z~ / ()D
County:.0f3F~
State: W A
SITIR:
Community 10:
Transect 10: '(.) p;/lr ~
Plot 10:
Investi ator(s): DJ~
Do Normal Circumstances exist on the site? yes no
Is the site significantly disturbed (atypical situation)? yes no
Is the area a potential Problem Area? yes no
Ex lanation of at ical or roblem area:
VEGETATION (For strata, indicate T = tree; S = shrub; H = herb; V = vine)
Dominant Plant S ecies
Stratum % cover Indicator Dominant Plant S ecies Stratum % cover
T 7~ 'ff\c:....
~ u .fkw
(00 f'
70
20
Indicator
% of dominants OBL, FACW, & FAC l DC%
Check all indicators that apply & explain below:
Visual observation of plant species growing in
areas of prolonged inundation/saturation ~
Morphological adaptations
Technical Literature
Hydrophytic vegetation present?
Rationale for decisionlRemarks:
Physiological/reproductive adaptations
Wetland plant database
Personal knowledge of regional plant communities
Other (ex lain)
~
-;z:-
HYDROLOGY
Is it the growing season?
6J
no
Water Marks: yes no
on
Drift Lines:
Sediment Deposits: yes no
Based on: pA-7I:::: soil temp (record temp.
other (ex lain)
Dept. of inundation: -D.... inches
yes no
Drainage Patterns: yes no
Depth to free water in pit: ~ inches
Depth to saturated soil: ~ inches
Check all that apply & explain below:
Stream, Lake or gage data:
Aerial hotoara hs: Other:
Wetland hydrology present? e
Rationale for decisionlRemarks:
Oxidized Root (live roots)
Channels <12 in. es no
FAC Neutral: yes no
Local Soil Survey: yes no
Water-stained Leaves yes no
Other (explain):
no
I SOILS
I Map Unit Name {Y\m
1 (Series & Phase)
lY1 '" (Y1c.JRMY st M vKtL. te'O Pc.~ DrainageClass II '^/
PiC- fYlEr;
r51
Field observations confirm
ma ed e?
@)
No
Profile Description
I Depth Horizon Matrix color Mottle colors Mottle abundance Texture, concretions, Drawing of soil
(inches) (Munsell (Munsell size & contrast structure, etc. profile
moist) moist) (match descriPtion)
i I D,rt- 3/ I YhOc(G
! 0-4 ....-
14lf 10'('(2.}Jl
~ .J,~
: 1-lD 16 Yr(. zll
I OVIZ-z[ t
- LO'ffZ5(1 "5TtN 0'1 10"
, 0- U:> IA 1/ '--
. ' -v 'UrtjL st f
Hydric Soil Indicators: (check all that apply)
- Histosol _ Matrix chroma s; 2 with mottles
_ Histic Epipedon _ Mg or Fe Concretions
- Sulfidic Odor _ High Organic Content in Surface Layer of Sandy Soils
_ Aquic Moisture Regime _ Organic Streaking in Sandy Soils
_ Reducing Conditions _ Listed on NationallLocal Hydric Soils List
Gleyed or Low-Chroma (=1) matrix Other (explain in remarks)
Hydric soils.present? yes no
Rationale for decision/Remarks:
Wetland Determination (circle)
Hydrophytic vegetation present? yes no
Hydric soils present? yes no Is the sampling point yes no
Wetland hydrolo~y present? yes no within a wetland?
RationalelRemarks: 11itS ~ l~ L..e5:!> Gtf>Tl>(lht;j:) - LT /hoP0<<" W t>(; ntC ~
~~ p~ /D Tlit':; \V~p.
.
NOTES:
Revised 4/97